Overview

Comprehensive Description

Description

A large-bodied salamander. Terrestrial adults have a light brown to dark brown dorsum with a yellowish to orange belly. The skin is dry with small bumps or warts and costal grooves are not visible. The eyes are large and the lower eyelids are yellow. Adult males in the breeding season develop smooth or slimy skin, a lighter body color, enlarged tail fins, and swollen cloacal glands (Storer, 1925; Stebbins, 1985). Adults are 6.9 - 8.7 cm snout to vent lenght (12.5 - 20 cm total length) (Stebbins 1985; Petranka 1998). Two allopatric subspecies are currently recognized based on geographic distribution (see below) and coloration. Taricha t. sierrae, the Sierra newt, is reddish to chocolate brown dorsally and burnt orange to yellow below. The eyelids and snout have conspicuous light coloring. Taricha t. torosa, the Coast Range newt, is yellowish to dark brown dorsally and pale yellow to orange ventrally. The eyelids and snout are not as conspicuously colored as in T. t. sierrae. (Riemer 1958; Stebbins 1985; Petranka 1998). Hatchlings are 10-14 mm total length. The larvae are pond type with bushy gills, balancer organs and a well-developed dorsal tail fin which extends forward to the shoulder region (Stebbins 1985; Petranka 1998). The dorsum of larvae is light yellow with two dark, narrow bands (Riemer 1958; Stebbins 1985).

Taricha torosa may be distinguished from close relatives (T. granulosa and T. rivularis) by the Y-shaped pattern of the vomerine teeth, the light-colored lower eyelids, relatively large eyes, and lack of a tomato red belly. The defensive posture differs between T. torosa and T. granulosa (see below) (Petranka 1998).
 
Extremely warty newts found in many localities in San Diego Co. have been described as a separate subspecies, T. t. klauberi (Riemer 1958). This subspecies is not currently recognized because the presence of warts is thought to be caused by a pathogenic agent (Stebbins 1951; 1985). Some authors have suggested recognizing the coastal and sierran forms as separate species (e.g. Collins 1991), but this suggestion has not been widely accepted (e.g. Petranka 1998).

See other subspecies accounts at www.californiaherps.com: T. t. sierrae and T. t. torosa.

  • Stebbins, R. C. (1985). A Field Guide to Western Reptiles and Amphibians. Houghton Mifflin, Boston.
  • Petranka, J. W. (1998). Salamanders of the United States and Canada. Smithsonian Institution Press, Washington and London.
  • Stebbins, R.C. (1951). Amphibians of Western North America. University of California Press, Berkeley.
  • Brodie, E. D., Jr. (1977). "Salamander antipredator postures." Copeia, 1977, 523-535.
  • Storer, T. I. (1925). "A synopsis of the amphibia of California." University of California Publications in Zoology, 27, 1-342.
  • Jennings, M. R., and Hayes, M. P. (1994). ''Amphibian and reptile species of special concern in California.'' Final Report #8023 Submitted to the California Department of Fish and Game. California Department of Fish and Game, Sacramento, California..
  • Collins, J. T. (1991). "A new taxonomic arrangement for some North American amphibians and reptiles." Herpetological Review, 22, 42-43.
  • Brodie, E. D., Jr., Hensel, J. L., and Johnson, J. A. (1974). ''Toxicity of the urodele amphibians Taricha, Notophthalmus, Cynops, and Paramesotriton (Family Salamandridae).'' Copeia, 1974(2), 506-511.
  • Riemer, W. J. (1958). "Variation and systematic relationships within the salamander genus Taricha." University of California Publications in Zoology, 56(3), 301-390.
  • Anzalone, C. R., Kats, L. B., and Gordon, M. S. (1998). "Effects of solar UV-B radiation on embryonic development in Hyla cadaverina, Hyla regilla, and Taricha torosa." Conservation Biology, 12(3), 646-653.
  • Blaustein, A. R., Hays, J. B., Hoffmann, P. D., and Kiescecker, J. M. (1998). "The role of solar UVB radiation in amphibian population declines." Photochemistry and Photobiology, 67(SPEC. ISSUE), 11S.
  • Gamradt, S. C. and Kats, L. B. (1996). ''Effect of introduced crayfish and mosquitofish on California newts.'' Conservation Biology, 10(4), 1155-1162.
  • Nussbaum, R. A., and Brodie, E. D., Jr. (1981). ''Taricha torosa (Rathke). California Newt.'' Catalogue of American Amphibians and Reptiles. Society for the Study of Amphibians and Reptiles, 273.1-273.4.
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Distribution

Range Description

Range includes the coast ranges of California, from Mendocino County southward to Los Angeles County and disjunctly south to the Cayumaca Mountains in San Diego County; also the southern Sierra Nevada from Tulare County to Kern County (Kuchta and Tan 2006). Taricha sierrae hybridizes with T. torosa in the southern Sierra Nevada (Kaweah River area) (Kuchta 2007).
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Geographic Range

The California Newt Taricha torosa is one of 5 members of the newt family (Salamandridae) which inhabit California. The California Newt is primarily located on the Coastal Range of California from Humbolt County to the Mexican border. Other isolated populations are also located in California, along the western slope of the Sierra Nevada mountain range (Petranka, 1998; Stebbins 1985; Dudek and Assoc., Inc. 2000).

Biogeographic Regions: nearctic (Native )

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endemic to a single state or province

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National Distribution

United States

Origin: Native

Regularity: Regularly occurring

Currently: Present

Confidence: Confident

Type of Residency: Year-round

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Global Range: (20,000-200,000 square km (about 8000-80,000 square miles)) Range includes the coast ranges of California, from Mendocino County southward to Los Angeles County and disjunctly south to the Cayumaca Mountains in San Diego County; also the southern Sierra Nevada from Tulare County to Kern County (Kuchta and Tan 2006). Taricha sierrae hybridizes with T. torosa in the southern Sierra Nevada (Kaweah River area) (Kuchta 2007).

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Distribution and Habitat

The Coast Range newt, T. t. torosa, ranges from Mendocino Co. south through the Coast Range to the western slope of the Peninsular ranges in San Diego Co. The southern-most locality (San Diego Co.) is isolated geographically from the remaining coastal populations. A gap in the distribution also exists in Santa Barbara Co. (Jennings and Hayes 1994; Stebbins 1985). The Sierra newt, T. t. sierrae, has a disjunct population in Shasta Co. and ranges along the western slopes of the Sierra Nevada south to Kern Co. (Stebbins 1985).

Terrestrial adults are found in mesic forests in relatively mountainous areas of northern California. Further south, they can be found in drier habitats such as oak woodlands or hilly grasslands. Sierran populations are found in habitats dominated by conifers (digger pines-blue oak and ponderosa pine communities) (Petranka 1998). Breeding sites include ponds, reservoirs, and slow moving streams. Sierran populations breed in faster moving streams than coastal populations (Stebbins 1985; Petranka 1998).

  • Stebbins, R. C. (1985). A Field Guide to Western Reptiles and Amphibians. Houghton Mifflin, Boston.
  • Petranka, J. W. (1998). Salamanders of the United States and Canada. Smithsonian Institution Press, Washington and London.
  • Stebbins, R.C. (1951). Amphibians of Western North America. University of California Press, Berkeley.
  • Brodie, E. D., Jr. (1977). "Salamander antipredator postures." Copeia, 1977, 523-535.
  • Storer, T. I. (1925). "A synopsis of the amphibia of California." University of California Publications in Zoology, 27, 1-342.
  • Jennings, M. R., and Hayes, M. P. (1994). ''Amphibian and reptile species of special concern in California.'' Final Report #8023 Submitted to the California Department of Fish and Game. California Department of Fish and Game, Sacramento, California..
  • Collins, J. T. (1991). "A new taxonomic arrangement for some North American amphibians and reptiles." Herpetological Review, 22, 42-43.
  • Brodie, E. D., Jr., Hensel, J. L., and Johnson, J. A. (1974). ''Toxicity of the urodele amphibians Taricha, Notophthalmus, Cynops, and Paramesotriton (Family Salamandridae).'' Copeia, 1974(2), 506-511.
  • Riemer, W. J. (1958). "Variation and systematic relationships within the salamander genus Taricha." University of California Publications in Zoology, 56(3), 301-390.
  • Anzalone, C. R., Kats, L. B., and Gordon, M. S. (1998). "Effects of solar UV-B radiation on embryonic development in Hyla cadaverina, Hyla regilla, and Taricha torosa." Conservation Biology, 12(3), 646-653.
  • Blaustein, A. R., Hays, J. B., Hoffmann, P. D., and Kiescecker, J. M. (1998). "The role of solar UVB radiation in amphibian population declines." Photochemistry and Photobiology, 67(SPEC. ISSUE), 11S.
  • Gamradt, S. C. and Kats, L. B. (1996). ''Effect of introduced crayfish and mosquitofish on California newts.'' Conservation Biology, 10(4), 1155-1162.
  • Nussbaum, R. A., and Brodie, E. D., Jr. (1981). ''Taricha torosa (Rathke). California Newt.'' Catalogue of American Amphibians and Reptiles. Society for the Study of Amphibians and Reptiles, 273.1-273.4.
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Physical Description

Morphology

Physical Description

The adult California Newt is typically 12.5-20 cm (4.9-7.8 inches) in total length with males slightly larger than females. California Newts vary in color from a yellowish brown to a dark brown warty textured skin dorsally and a pale yellow to orange bottom on its ventral side. The aquatic larvae have a black stripe on either side of their dorsal fins and have gills in younger stages of development. They have large eyes that protrude beyond the edge of their head and light colored lower eyelids. (Petranka, 1998; Stebbins & Cohen, 1998).

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Type Information

Syntype for Taricha torosa
Collection: Smithsonian Institution, National Museum of Natural History, Department of Vertebrate Zoology, Division of Amphibians & Reptiles
Preparation: Ethanol
Locality: San Francisco, California, United States, North America
  • Syntype: Baird, S. F. & Girard, C. 1853. Proc. Acad. Nat. Sci. Philadelphia. 6: 301.
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Ecology

Habitat

Habitat and Ecology

Habitat and Ecology
Breeding occurs in ponds, reservoirs, and streams, and terrestrial individuals occupy various adjacent upland habitats such as grassland, woodland, and forest (Storer 1925, Petranka 1998, Stebbins 2003, Kuchta 2005). Eggs are attached to sticks, undersides of stones, or vegetation in flowing or nonflowing water; fast-moving streams and rivers are used more often in Sierra Nevada foothills and in southern California mountains than elsewhere in the range.

Systems
  • Terrestrial
  • Freshwater
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Habitat

The California Newt of the northern population prefers the mesic forests as opposed to the southern population newts which prefer a drier climate (Petranka, 1998).

Aquatic Biomes: lakes and ponds; rivers and streams

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Comments: When not breeding, coast range newts occupy various upland habitats such as grassland, woodland, and forest(Storer 1925, Petranka 1998, Stebbins 2003, Kuchta 2005).. Breeding occurs in ponds, reservoirs, and streams. Eggs are attached to sticks, stones, or vegetation in flowing or nonflowing water; fast-moving streams and rivers are used more often in southern California mountains than elsewhere in the range.

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Migration

Non-Migrant: No. All populations of this species make significant seasonal migrations.

Locally Migrant: Yes. At least some populations of this species make local extended movements (generally less than 200 km) at particular times of the year (e.g., to breeding or wintering grounds, to hibernation sites).

Locally Migrant: No. No populations of this species make annual migrations of over 200 km.

Coast range newts sometimes migrate long distances (up to around two miles) between nonbreeding uplands habitats and distant aquatic breeding sites, though movements may be much shorter when conditions near breeding sites are favorable. Unfortunately, many are killed on roads as they make their migrations.

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Trophic Strategy

Food Habits

The diet of an adult California Newt consists of earthworms, snails, slugs, and sowbugs. Adult newts have also been known to cannibalize their own eggs and larvae. There is little known about the diets of the California Newt during the larvae stage.

 The California Newt has an adhesive texture to its tongue and projects it out to capture its prey.

(Petranka, 1998; Dudek and Assoc., Inc. 2000, Deban 1996).

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Comments: Metamorphosed individuals eat earthworms, snails, slugs, sowbugs, and various insects; adults, especially females, may eat conspecific eggs. Larvae eat small aquatic organisms and decomposing organic material (Stebbins 1951).

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Population Biology

Number of Occurrences

Note: For many non-migratory species, occurrences are roughly equivalent to populations.

Estimated Number of Occurrences: 81 - 300

Comments: This species is represented by many and/or large occurrences throughout most of the range.

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Global Abundance

100,000 - 1,000,000 individuals

Comments: Total adult population size is unknown but surely exceeds 100,000. This species is common in many parts of its range.

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Life History and Behavior

Cyclicity

Comments: Coast range newts are inactive in cold temperatures or hot, dry weather. They often are active in daylight during the rainy season.

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Life Expectancy

Lifespan/Longevity

Average lifespan

Status: captivity:
21.8 years.

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Lifespan, longevity, and ageing

Maximum longevity: 21.8 years (captivity)
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Reproduction

Reproduction

Mating for the California Newt takes place from December to early May. The California Newt often migrates back to breed where they developed as larvae. Courtship of the California Newt involves a dance ritual in which the male mounts the female and rubs his chin over her nose and flutters his tail. After approximately an hour the male dismounts and leaves a spermatophore, in the form of a small mound, for the female move over and retrieve with her cloaca. The female California Newt will lay their eggs in ponds, lakes, and slow moving streams in water typically not deeper than 15 cm (5 inches). They lay from 7-30 eggs (approximately 1.9-2.8mm in diameter), attached to exposed roots or unattached on the bottom. The eggs are protected by a gel-like membrane that is toxic. The incubation period is usually 14-21 days and often longer depending on weather conditions. The size and amount of time in the larvae stage depends on the food sources and environmental conditions of their habitat (Petranka, 1998; Duellman, 1986).

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Coast range newts migrate seasonally between upland habitats and aquatic breeding sites. Generally they begin moving to water with the first fall rains. Breeding occurs from December to May (peak February-April). Individual females lay 1 or 2 dozen eggs in spherical masses. Larvae hatch in about 4-8 weeks. Larvae transform in late summer or early fall or when the water dries up. Metamorphosed juveniles live several years on land before maturing and returning to water to breed.

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Conservation

Conservation Status

IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2008

Assessor/s
Geoffrey Hammerson

Reviewer/s
Global Amphibian Assessment Coordinating Team (Simon Stuart, Janice Chanson, Neil Cox and Bruce Young)

Justification
Listed as Least Concern in view of its wide distribution, tolerance of a broad range of habitats, presumed large population, and because it is unlikely to be declining fast enough to qualify for listing in a more threatened category.

History
  • 2004
    Least Concern
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Conservation Status

The California Newt is not currently listed as an endangered species but there is to be a significant problem in the Santa Monica Mountains with non-native crayfish (Procambarus clarkii) and mosquitofish (Gambusia affiinis) feeding on the eggs and larvae of the California Newt. (Petranka, 1998).

US Federal List: no special status

CITES: no special status

IUCN Red List of Threatened Species: least concern

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National NatureServe Conservation Status

United States

Rounded National Status Rank: N4 - Apparently Secure

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NatureServe Conservation Status

Rounded Global Status Rank: G4 - Apparently Secure

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Population

Population
This species is represented by many and/or large occurrences throughout most of the range. Total adult population size is unknown but surely exceeds 100,000. This species is common in many parts of its range. Over the long term, likely relatively stable in extent of occurrence, probably less than 25% decline in population size, area of occurrence, and number/condition of occurrences. Many historical occurrences in San Diego County appear to be extirpated. Currently relatively stable in extent of occurrence; probably relatively stable to slowly declining in population size, area of occurrence, and number/condition of occurrences.

Population Trend
Unknown
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Global Short Term Trend: Relatively stable to decline of 30%

Comments: Currently relatively stable in extent of occurrence; probably relatively stable to slowly declining in population size, area of occurrence, and number/condition of occurrences.

Global Long Term Trend: Increase of 10-25% to decline of 30%

Comments: Over the long term, likely relatively stable in extent of occurrence, probably less than 25% decline in population size, area of occurrence, and number/condition of occurrences. Many historical occurrences in San Diego County appear to be extirpated.

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Life History, Abundance, Activity, and Special Behaviors

The breeding season ranges from late December and early May, depending on location, and lasts 6-12 weeks. Breeding aggregations form primarily in ponds and lakes. Stream-breeding is more common in sierran populations and tends to occur late in the season for coastal populations. Courtship involves amplexus of the female by the male who then rubs his head on hers. Eventually the male deposits a spermatophore on the substrate which the female picks up in her cloaca. Shortly after mating, the female lays her eggs in small clusters containing 7-30 eggs. Time to hatching ranges from 2 weeks to 2 1/2 months, depending on water temperature. Diet items include earthworms, snails, slugs, insects, and conspecific eggs and larvae. See Petranka (1998) for references.

All species of Taricha possess the potent neurotoxin tetrodotoxin, that is used as an antipredator defense (Brodie et al. 1974). Tetrodotoxin is also harmful to humans (e.g. Petranka 1998). When harassed, Taricha assume the "unken reflex" where the head is raised, the tail is turned up and held straight over the body, the limbs are extended, and the eyes are closed (Riemer 1958; Brodie 1977). This action exposes the bright aposomatic coloration found on the newt's belly. The exact pattern of this reflex is a species-specific character, distinguishable from sympatric T. granulosa, which curls the tip of the tail (Stebbins 1985; Petranka 1998).

  • Stebbins, R. C. (1985). A Field Guide to Western Reptiles and Amphibians. Houghton Mifflin, Boston.
  • Petranka, J. W. (1998). Salamanders of the United States and Canada. Smithsonian Institution Press, Washington and London.
  • Stebbins, R.C. (1951). Amphibians of Western North America. University of California Press, Berkeley.
  • Brodie, E. D., Jr. (1977). "Salamander antipredator postures." Copeia, 1977, 523-535.
  • Storer, T. I. (1925). "A synopsis of the amphibia of California." University of California Publications in Zoology, 27, 1-342.
  • Jennings, M. R., and Hayes, M. P. (1994). ''Amphibian and reptile species of special concern in California.'' Final Report #8023 Submitted to the California Department of Fish and Game. California Department of Fish and Game, Sacramento, California..
  • Collins, J. T. (1991). "A new taxonomic arrangement for some North American amphibians and reptiles." Herpetological Review, 22, 42-43.
  • Brodie, E. D., Jr., Hensel, J. L., and Johnson, J. A. (1974). ''Toxicity of the urodele amphibians Taricha, Notophthalmus, Cynops, and Paramesotriton (Family Salamandridae).'' Copeia, 1974(2), 506-511.
  • Riemer, W. J. (1958). "Variation and systematic relationships within the salamander genus Taricha." University of California Publications in Zoology, 56(3), 301-390.
  • Anzalone, C. R., Kats, L. B., and Gordon, M. S. (1998). "Effects of solar UV-B radiation on embryonic development in Hyla cadaverina, Hyla regilla, and Taricha torosa." Conservation Biology, 12(3), 646-653.
  • Blaustein, A. R., Hays, J. B., Hoffmann, P. D., and Kiescecker, J. M. (1998). "The role of solar UVB radiation in amphibian population declines." Photochemistry and Photobiology, 67(SPEC. ISSUE), 11S.
  • Gamradt, S. C. and Kats, L. B. (1996). ''Effect of introduced crayfish and mosquitofish on California newts.'' Conservation Biology, 10(4), 1155-1162.
  • Nussbaum, R. A., and Brodie, E. D., Jr. (1981). ''Taricha torosa (Rathke). California Newt.'' Catalogue of American Amphibians and Reptiles. Society for the Study of Amphibians and Reptiles, 273.1-273.4.
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Threats

Threats

Major Threats
Under natural conditions, solar UV-B radiation reduces embryo survival; effects at the population level remain to be determined (Anzalone et al. 1998).

Introduced crayfish and mosquitofish (Gambusia) prey on eggs and larvae and have caused local population declines in southern California (Gamradt and Kats 1996). Introduced fishes likely have a negative impact in some bodies of water.

Locally, population have been reduced or eliminated as a result of habitat degradation or loss caused by conversion of habitat to human uses and to a much lesser degree by large-scale commercial exploitation (Jennings and Hayes 1994). Increased stream sedimentation resulting from erosion caused by human activities and wildlfires (Gamradt and Kats 1997, Kerby and Kats 1998) has degraded breeding habitat in some areas (Jennings and Hayes 1994).

Many are killed on roads as they move between uplands and aquatic breeding sites.
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Comments: Under natural conditions, solar UV-B radiation reduces embryo survival; effects at the population level remain to be determined (Anzalone et al. 1998).

Introduced crayfish and mosquitofish (Gambusia) prey on eggs and larvae and have caused local population declines in southern California (Gamradt and Kats 1996). Introduced fishes likely have a negative impact in some bodies of water.

Locally, population have been reduced or eliminated as a result of habitat degradation or loss caused by conversion of habitat to human uses and to a much lesser degree by large-scale commercial exploitation (Jennings and Hayes 1994). Increased stream sedimentation resulting from erosion caused by human activities and wildlfires (Gamradt and Kats 1997, Kerby and Kats 1998) has degraded breeding habitat in some areas (Jennings and Hayes 1994).

Many are killed on roads as they move between uplands and aquatic breeding sites.

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Life History, Abundance, Activity, and Special Behaviors

Loss and degradation of stream habitats, and predation on eggs and larvae by introduced predators such as crayfish and mosquitofish, are a serious concern for populations of T. t. torosa in southern California (Jennings and Hayes 1994; Gamradt and Kats 1996). Road-kill is also a large source of adult mortality. Furthermore, UV-B radiation has been shown to cause reduced hatching success (Anzalone et al. 1998; Blaustein et al. 1998).
  • Stebbins, R. C. (1985). A Field Guide to Western Reptiles and Amphibians. Houghton Mifflin, Boston.
  • Petranka, J. W. (1998). Salamanders of the United States and Canada. Smithsonian Institution Press, Washington and London.
  • Stebbins, R.C. (1951). Amphibians of Western North America. University of California Press, Berkeley.
  • Brodie, E. D., Jr. (1977). "Salamander antipredator postures." Copeia, 1977, 523-535.
  • Storer, T. I. (1925). "A synopsis of the amphibia of California." University of California Publications in Zoology, 27, 1-342.
  • Jennings, M. R., and Hayes, M. P. (1994). ''Amphibian and reptile species of special concern in California.'' Final Report #8023 Submitted to the California Department of Fish and Game. California Department of Fish and Game, Sacramento, California..
  • Collins, J. T. (1991). "A new taxonomic arrangement for some North American amphibians and reptiles." Herpetological Review, 22, 42-43.
  • Brodie, E. D., Jr., Hensel, J. L., and Johnson, J. A. (1974). ''Toxicity of the urodele amphibians Taricha, Notophthalmus, Cynops, and Paramesotriton (Family Salamandridae).'' Copeia, 1974(2), 506-511.
  • Riemer, W. J. (1958). "Variation and systematic relationships within the salamander genus Taricha." University of California Publications in Zoology, 56(3), 301-390.
  • Anzalone, C. R., Kats, L. B., and Gordon, M. S. (1998). "Effects of solar UV-B radiation on embryonic development in Hyla cadaverina, Hyla regilla, and Taricha torosa." Conservation Biology, 12(3), 646-653.
  • Blaustein, A. R., Hays, J. B., Hoffmann, P. D., and Kiescecker, J. M. (1998). "The role of solar UVB radiation in amphibian population declines." Photochemistry and Photobiology, 67(SPEC. ISSUE), 11S.
  • Gamradt, S. C. and Kats, L. B. (1996). ''Effect of introduced crayfish and mosquitofish on California newts.'' Conservation Biology, 10(4), 1155-1162.
  • Nussbaum, R. A., and Brodie, E. D., Jr. (1981). ''Taricha torosa (Rathke). California Newt.'' Catalogue of American Amphibians and Reptiles. Society for the Study of Amphibians and Reptiles, 273.1-273.4.
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Management

Conservation Actions

Conservation Actions
None needed. Many occurrences are in protected areas.
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Relevance to Humans and Ecosystems

Risks

Relation to Humans

No known relation.
  • Stebbins, R. C. (1985). A Field Guide to Western Reptiles and Amphibians. Houghton Mifflin, Boston.
  • Petranka, J. W. (1998). Salamanders of the United States and Canada. Smithsonian Institution Press, Washington and London.
  • Stebbins, R.C. (1951). Amphibians of Western North America. University of California Press, Berkeley.
  • Brodie, E. D., Jr. (1977). "Salamander antipredator postures." Copeia, 1977, 523-535.
  • Storer, T. I. (1925). "A synopsis of the amphibia of California." University of California Publications in Zoology, 27, 1-342.
  • Jennings, M. R., and Hayes, M. P. (1994). ''Amphibian and reptile species of special concern in California.'' Final Report #8023 Submitted to the California Department of Fish and Game. California Department of Fish and Game, Sacramento, California..
  • Collins, J. T. (1991). "A new taxonomic arrangement for some North American amphibians and reptiles." Herpetological Review, 22, 42-43.
  • Brodie, E. D., Jr., Hensel, J. L., and Johnson, J. A. (1974). ''Toxicity of the urodele amphibians Taricha, Notophthalmus, Cynops, and Paramesotriton (Family Salamandridae).'' Copeia, 1974(2), 506-511.
  • Riemer, W. J. (1958). "Variation and systematic relationships within the salamander genus Taricha." University of California Publications in Zoology, 56(3), 301-390.
  • Anzalone, C. R., Kats, L. B., and Gordon, M. S. (1998). "Effects of solar UV-B radiation on embryonic development in Hyla cadaverina, Hyla regilla, and Taricha torosa." Conservation Biology, 12(3), 646-653.
  • Blaustein, A. R., Hays, J. B., Hoffmann, P. D., and Kiescecker, J. M. (1998). "The role of solar UVB radiation in amphibian population declines." Photochemistry and Photobiology, 67(SPEC. ISSUE), 11S.
  • Gamradt, S. C. and Kats, L. B. (1996). ''Effect of introduced crayfish and mosquitofish on California newts.'' Conservation Biology, 10(4), 1155-1162.
  • Nussbaum, R. A., and Brodie, E. D., Jr. (1981). ''Taricha torosa (Rathke). California Newt.'' Catalogue of American Amphibians and Reptiles. Society for the Study of Amphibians and Reptiles, 273.1-273.4.
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Wikipedia

California Newt

The California newt (Taricha torosa) is a newt. It is also referred to as the orange bellied newt. They can grow to be 8 inches (20 cm) in length.

Contents

Physical description

T. torosa adult length can range from 5 inches (13 cm) to 8 inches (20 cm). [1]

Subspecies

California newts are divided into two subspecies:

The difference between these two seems to be only in the location in which the newt is found.

Range and habitat

California newts exist primarily on the California coastline and in the Sierra Nevada. This is because they prefer less humid climates than the rough skinned newts. During the non-breeding season the newts are land dwelling, preferring rock crevices and logs. While breeding, the subspecies torosa torosa prefers slow moving pools in coastal streams.[citation needed]

Reproduction

Reproduction occurs generally between December and early May. Typically the adult newts will return to the pool in which they hatched. After a mating dance, the male mounts the female and rubs his chin on her nose. He then attaches a spermatophore to the substrate, which she will retrieve into her cloaca.

The egg mass released by the female contains between 7 and 30 eggs, and is roughly the consistency of a thick gelatin dessert. Typically the egg masses are attached to stream plant roots or to rocky crevices in small, slow moving pools. But they have also been known to be attached to underwater rocks or leaf debris. While shallow in a wide sense, these pools are rather deep relative to the average depth of a Southern California stream, varying in depth from about 1 to 2 meters.

Adult newts will stay in the pools throughout the breeding season, and can be occasionally found well into the summer. Larvae hatch sometime in early to mid summer, depending on local water temperature. Larvae are difficult to find in streams as they blend in well with the sandy bottom, which they usually stay close to.

Toxicity and predation

Like other Taricha members, the glands in the skin of T. torosa secrete the potent neurotoxin tetrodotoxin, which is hundreds of times more toxic than cyanide. This is the same toxin found in pufferfish and harlequin frogs. Researchers believe that bacteria synthesize tetrodotoxin and the animals that employ the neurotoxin acquire it through consumption of these bacteria. This neurotoxin is so strong that it is enough to kill most vertebrates, including humans. However, they are dangerous only if ingested, and can be safely kept as pets.

Due to their toxicity, the California newt has few natural predators. Garter snakes are the most common, and some species have developed a genetic resistance to tetrodotoxin.

Diet

Earthworms, snails, slugs, sowbugs, bloodworms, mosquito larvae and other invertebrates are among the California newt's prey. In the Sierra, the newt will also consume trout eggs. In an aquarium habitat, it is recommended that they continue to be fed earthworms, as they provide the newt with all of the necessary nutrients. Other natural prey items would benefit the captive newt. Pellets tend to be inappropriate for terrestrial caudates and fish food should be avoided completely.

Conservation status

California newt in a Southern Californian riparian habitat.

The California newt is currently a California Special Concern species (DFG-CSC). Some populations have been greatly reduced in southern California coastal streams due to the introduction of non-native, invasive species and human habitation. The mosquitofish (Gambusia affinis) and red swamp crayfish (Procambarus clarkii) have caused the greatest reduction in newt populations.

Introduced as fish bait and stock pond prey, red swamp crayfish are an incredibly aggressive, prolific, and stalwart species that will prey upon newt larvae and egg masses. The crayfish will also disrupt newt breeding via competition for space during the summer mating season and physically antagonizing adults. Crayfish will typically maul the adult newts with their claws, and subsequent infection can lead to death. T. torosa are present in streams with introduced crayfish often sport tails with several notches removed. They are amphibians and live in humid areas.

See also

References

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Names and Taxonomy

Taxonomy

Comments: Taricha sierrae formerly was recognized as a subspecies of Taricha torosa.

Phylogenetic analysis of mtDNA data (Tan and Wake 1995) revealed the following clusters in T. torosa: (1) northern Sierra Nevada (Shasta to Nevada counties); (2) central Sierra Nevada (El Dorado to Fresno counties); (3) southern Sierra Nevada (Tulare to Kern counties) (independently derived relative to 1 and 2, above); (4) southern coastal California (San Diego and Orange counties); (5) central coastal California (Los Angeles to central and northern California). This study and additional allozyme data (Kuchta and Tan 2006) provided the basis for a phylogeographical history of T. torosa. Among other things, the data are consistent in indicating that populations in the southern Sierra Nevada are more closely related to T. torosa torosa than to T. t. sierrae.

In the interests of taxonomic stability, Kuchta and Tan (2006) refrained from advocating changes in the taxonomic status of Taricha torosa torosa and Taricha torosa sierrae, pending completion and publication of ongoing studies.

Kuchta (2007) examined genetic and morphological variation in Taricha torosa and concluded that T. torosa and T. sierrae are distinct evolutionary lineages that should be recognized as distinct species.

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